Birds
Great Horned Owl (Bubo virginianus)
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Sample Size | Location | Type | Countries |
|---|---|---|---|---|---|---|---|---|
| Dietary Composition | Townsend vole: 57.3, pacific jumping mouse: 1.3, rat species: 33.4, eastern cottontail: 2.7, medium songbirds: 1.3, American crow: 1.3, family anatidae: 1.3, order coleoptera: 1.3 | Percent by number in pellets/prey remains | % | NR | Central Surrey | Exposure Factor Datasets | CANADA | |
| Dietary Composition | Townsend vole: 84.8, common muskrat: 1.0, rat species: 1.0, medium songbirds: 5.1, family anatidae: 5.1, order coleoptera: 3.0 | Percent by number in pellets/prey remains | % | NR | See citation | Alaskan National Wildlife Area | Exposure Factor Datasets | CANADA |
| Dietary Composition | Townsend vole: 97.5, rat species: 2.5 | Percent by number in pellets/prey remains | % | NR | See citation | Arthur Drive | Exposure Factor Datasets | CANADA |
| Dietary Composition | Townsend vole: 2.1, North American deer mouse: 21.3, rat species: 42.6, order lagomorpha: 2.1, eastern cottontail: 4.3, medium songbirds: 10.6, small songbirds: 6.4, American crow: 4.3, order coleoptera: 6.4 | Percent by number in pellets/prey remains | % | NR | See citation | Crescent Park | Exposure Factor Datasets | CANADA |
| Dietary Composition | Townsend vole: 37.3, rat species: 25.5, eastern cottontail: 23.5, coast mole: 5.9, medium songbirds: 2.0, small songbirds: 2.0, American crow: 2.0, family anatidae: 2.0 | Percent by number in pellets/prey remains | % | NR | See citation | Beach Groove Park | Exposure Factor Datasets | CANADA |
| Dietary Composition | Townsend vole: 70.3, North American deer mouse: 1.4, rat species: 1.4, shrew species: 9.5, American crow: 2.7, great blue heron: 1.4, barn owl: 10.8, order coleoptera: 2.7 | Percent by number in pellets/prey remains | % | NR | See citation | Terra Nova Park | Exposure Factor Datasets | CANADA |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
|---|---|---|---|---|---|---|---|---|---|
| Dietary Composition | Mammalia: 95.74, aves: 0.85 | Percent biomass in undisturbed site | % | B | Not Reported | 2448 | US Army Dugway Proving Ground | Exposure Factor Datasets | USA |
| Dietary Composition | Mammalia: 89.76, aves: 7.07 | Percent biomass in disturbed site | % | B | Not Reported | 1478 | US Army Dugway Proving Ground | Exposure Factor Datasets | USA |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
|---|---|---|---|---|---|---|---|---|---|
| Dietary Composition | Class aves: 24.8, class mammalia: 75.2, class crustacae: 0.0 | Percent biomass | % | NR | Not Reported | 285 | Trowbridge | Exposure Factor Datasets | USA |
| Dietary Composition | Class aves: 13.8, class mammalia: 86.2, class crustacae: 0.0 | Percent biomass | % | NR | Not Reported | 285 | Fort Cluster | Exposure Factor Datasets | USA |
Double-crested Cormorant (Phalacrocorax auritus)
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Location | Type | Countries |
|---|---|---|---|---|---|---|---|---|
| Population Density | See citation Table 1 | Adults/sq km | Adults/sq km | NR | Adult | North Channel, Lake Huron | Exposure Factor Datasets | CANADA |
| Population Density | See citation Table 1 | Adults/sq km | Adults/sq km | NR | Adult | Georgian Bay, Lake Huron | Exposure Factor Datasets | CANADA |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Life Cycle Stage | Location | Type | Countries |
|---|---|---|---|---|---|---|
| Survival/ Mortality | See citation Figure 4 | Second-year birds | Adult | Great Lakes region | Exposure Factor Datasets | USA |
| Survival/ Mortality | See citation Figure 5 | Hatch-year birds | Juvenile | Great Lakes region | Exposure Factor Datasets | USA |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Life Cycle Stage | Location | Type | Countries |
|---|---|---|---|---|---|---|---|
| Survival/ Mortality | 0.696 | Survival, modeled average (Adult, at least 2 y) | Percent | Adult | Lake Michigan | Exposure Factor Datasets | USA |
| Survival/ Mortality | 0.305 | Survival, modeled average (first year) | Percent | Juvenile | Lake Michigan | Exposure Factor Datasets | USA |
| Survival/ Mortality | 0.774 | Survival, modeled average (Second/third year) | Percent | Juvenile | Lake Michigan | Exposure Factor Datasets | USA |
| Survival/ Mortality | 0.633 | Survival, modeled average (Adult, at least 4 y) | Percent | Adult | Lake Michigan | Exposure Factor Datasets | USA |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Life Cycle Stage | Sample Size | Location | Type | Countries |
|---|---|---|---|---|---|---|---|---|
| Dietary Composition | Striped mullet: 25.5, gulf menhaden: 17.6, hardhead catfish: 11.8, Sciaendiae: 15.7, unidentifiable fish: 5.9 | Frequency | % | Not Reported | 51 | Lavaca bay | Exposure Factor Datasets | USA |
| Dietary Composition | Striped mullet: 28.5, hardhead catfish: 2.5, gulf toadfish: 46.4 Sciaendiae: 0, unidentifiable fish: 3.6 | Frequency | % | Not Reported | 28 | Laguna Madre | Exposure Factor Datasets | USA |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Location | Type | Countries |
|---|---|---|---|---|---|
| Population Density | See citation | Breeding pairs/location | Exposure Factor Datasets | USA |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Location | Type | Countries |
|---|---|---|---|---|---|---|---|---|
| Dietary Composition | 2006: >93% alewife, 2007: 86.5%; balance made up of round goby, rainbow smelt, pumpkinseed | Chick diet | % by mass | B | Adult | Tommy Thompson Park, Lake Ontario | Exposure Factor Datasets | CANADA |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
|---|---|---|---|---|---|---|---|---|---|
| Clutch or Litter Size | 2008: 1.79 ± 0.03, 2009: 1.96 ± 0.02 | Brood size | Number of hatchlings | NR | Hatchling | 2008: 493 nests, 2009: 559 nests | Northeast SD | Exposure Factor Datasets | USA |
| Time of Hatching or Parturition | 2008: June 4, 2009: May 29 | Earliest hatch date | Hatchling | 2008: 493 nests, 2009: 559 nests | Northeast SD | Exposure Factor Datasets | USA | ||
| Hatching Success | 2008: 49.5% [45.9-52.9 (95% CI)], 2009: 59.4% [55.8-63.1 (95% CI)] | Fledge success | Hatchling | 2008: 28, 2009: 25 | Northeast SD | Exposure Factor Datasets | USA |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Life Cycle Stage | Location | Type | Condition | Countries |
|---|---|---|---|---|---|---|---|
| Population Density | See citation Figure 2 | Active nests/11,000 ha | Adult | Estero Bay Aquatic Preserve | Exposure Factor Datasets | Breeding | USA |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
|---|---|---|---|---|---|---|---|---|---|
| Dietary Composition | Herring, shad: 0.6, Peamouth/Pikeminnow: 24.0, Sucker: 5.8, Smelt: 0.3, Salmonid: 45.5, Stickleback: 5.0, Sculpin: 8.0, Surfperch: 0.3, Flounder: 8.5, Other: 1.8 | Percent by mass from adult foregut and chick regurgitation samples | % | NR | Both Adults and Juveniles | 206 | Rice Island/Channel Markers | Exposure Factor Datasets | USA |
| Dietary Composition | Herring, shad: 27.8, Peamouth/Pikeminnow: 0.7, Sucker: 4.7, Smelt: 7.6, Salmonid: 15.9, Stickleback: 2.1, Sculpin: 9.2, Surfperch: 7.3, Flounder: Pacific sand lance: 1.8, Flounder: 9.8 Other: 1.3 | Percent by mass from adult foregut and chick regurgitation samples | % | NR | Both Adults and Juveniles | 128 | East Sand Island | Exposure Factor Datasets | USA |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Location | Type | Countries |
|---|---|---|---|---|---|---|
| Dietary Composition | Cyprinid, Lepomis spp., rainbow smelt, rock bass, white perch, yellow perch | Percent by number before alewife eastablishment | % | Exposure Factor Datasets | USA | |
| Dietary Composition | Alewife ,cyprinid, Lepomis spp., rainbow smelt, rock bass, white perch, yellow perch | Percent by number after alewife eastablishment | % | Exposure Factor Datasets | USA |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Location | Type | Countries |
|---|---|---|---|---|---|---|
| Dietary Composition | See citation | Percent by number | % | Lake Oneida | Exposure Factor Datasets | USA |
| Dietary Composition | See citation | Percent by number | % | Lake Oneida | Exposure Factor Datasets |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Location | Type | Age-Specific | Countries |
|---|---|---|---|---|---|---|---|---|
| Dietary Composition | See citation | Percent composition and biomass | B | Adult | Exposure Factor Datasets | Leech Lake | USA | |
| Dietary Composition | See citation | Percent composition and biomass | B | Chick | Exposure Factor Datasets | Leech Lake | USA |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
|---|---|---|---|---|---|---|---|---|---|
| Dietary Composition | Pre-goby: 14.4, Transition 14.3, Post-goby: 20.1 | Number of fish eaten per pellet by different periods | Numerb of fish | NR | Adult | Pre-goby: 3100, Transition 2206, Post-goby: 1028 | Griswold Island | Exposure Factor Datasets | CANADA |
| Dietary Composition | Pre-goby: 11.9, Transition 12.7, Post-goby: 16.7 | Number of fish eaten per pellet by different periods | Numerb of fish | NR | Adult | Pre-goby: 923, Transition 1631, Post-goby: 2035 | McNair Island | Exposure Factor Datasets | CANADA |
| Dietary Composition | Pre-goby: 13.2, Transition 12.8, Post-goby: 17.0 | Number of fish eaten per pellet by different periods | Numerb of fish | NR | Adult | Pre-goby: 1187, Transition 518, Post-goby: 1404 | Strachan Island | Exposure Factor Datasets | CANADA |
| Dietary Composition | See citation Table 4 | Percent species by number by different periods | % | NR | Not Reported | See citation | Three sites along St. Lawrence River | Exposure Factor Datasets | CANADA |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
|---|---|---|---|---|---|---|---|---|---|
| Dietary Composition | Pre-goby: 10.15, Transition 10.25, Post-goby: 14.81 | Number of fish eaten per pellet by different periods | Numerb of fish | NR | Not Reported | Pre-goby: 17,681, Transition 1800, Post-goby: 4662 | Lilttle Galloo Island, Lake Ontario | Exposure Factor Datasets | CANADA |
| Dietary Composition | See citation Table 4 | Percent species by number by different periods | % | NR | Not Reported | Pre-goby: 17,681, Transition 1800, Post-goby: 4662 | Lilttle Galloo Island, Lake Ontario | Exposure Factor Datasets | CANADA |
| Exposure Endpoint Type | Endpoint Value | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Condition | Countries | Error |
|---|---|---|---|---|---|---|---|---|---|---|
| Home Range | 17490 sq km | sq km | B | Adult | 37 | Mississipi Alluvial Valley (AR, MS, LA) & Upper Coastal Plain (AL, MS) | Exposure Factor Datasets | Over-wintering populations | USA | 1986 |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Location | Type | Condition | Countries |
|---|---|---|---|---|---|---|---|
| Population Density | 1990: 3985, 1994: 9854, 1997: 8217, 2000: 12821, 2003: 11470 | Number of nests | Number of nests | Georgian Bay, Lake Huron | Exposure Factor Datasets | Breeding | CANADA |
| Population Density | 1990: 4310, 1994: 7281, 1997: 8494, 2000: 12441, 2003: 11527 | Number of nests | Number of nests | North Channel, Lake Huron | Exposure Factor Datasets | Breeding | CANADA |
Least Tern (Sterna antillarum)
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Life Cycle Stage | Sample Size | Location | Type | Countries |
|---|---|---|---|---|---|---|---|---|
| Hatching Success | 1995: 0.97, 1996: 0.03, 1997: 0.93 | Ratio of hatched eggs:total eggs | Embryo | 1995: 1472, 1996: 624, 1997: 349 | Cow Island, lower Mississippi River | Exposure Factor Datasets | USA | |
| Time of Mating/ Laying | 1995: 179, 1996: 182, 1997: 161 | Clutch initiation dates | Julian date | Embryo | 1995: 240, 1996: 161, 1997: 481 | Kangaroo Pt., lower Mississippi River | Exposure Factor Datasets | USA |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Location | Type | Countries |
|---|---|---|---|---|---|---|---|
| Hatching Success | 0.67 | Fledglings/pair | NR | Fledgling | Arkansas River at Tulsa | Exposure Factor Datasets | USA |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sample Size | Location | Type | California Counties | Countries |
|---|---|---|---|---|---|---|---|
| Hatching Success | Review | Fledglings per nest | 522 | Venice Beach | Exposure Factor Datasets | Los Angeles | USA |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Location | Type | Countries |
|---|---|---|---|---|---|---|---|---|
| Hatching Success | 0.14-0.74 | Fledging success | Number of fledgings/number of hatched chicks | NR | Fledgling | Towsn of Wells & Kennebunk | Exposure Factor Datasets | USA |
Loggerhead Shrike (Lanius ludovicianus)
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sample Size | Location | Type | Countries |
|---|---|---|---|---|---|---|
| Dietary Composition | Chaetodipus arenarius (11.0), Chaetopidus baileyi (20.5), Peromyscus eva (15.0) | Species captured (mean weight, g) | Not reported | Baja California Sur | Exposure Factor Datasets | MEXICO |
Killdeer (Charadrius vociferus)
| Exposure Endpoint Type | Endpoint Value | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries | Error |
|---|---|---|---|---|---|---|---|---|---|
| Home Range | Winter residents: 7.73 sq km, year-round residents: 2.28 sq km | sq km | NR | Adult | Winter residents: 249, year-round residents: 86 | Willamette Valley | Exposure Factor Datasets | USA | Winter residents: 3.19 sq km, year-round residents: 2.05 sq km |
Burrowing Owl (Athene cunicularia)
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
|---|---|---|---|---|---|---|---|---|---|
| Dietary Composition | Vertebrates: 362, Arthropods: 233.2 | Percent of total prey biomass | % | NR | Not Reported | 2 | Tall Grass Prairie National Preserve | Exposure Factor Datasets | USA |
| Dietary Composition | See citation Figure 2 | Percent of total prey biomass at different breeding stages | % | NR | Not Reported | 2 | Tall Grass Prairie National Preserve | Exposure Factor Datasets | USA |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Location | Type | Condition | Countries |
|---|---|---|---|---|---|---|---|---|
| Population Density | 1993: 7.2, 1994: 1.9, 1995: 11.6, 1997: 13.5, 1998: 9.7, 1999: 9.7, 2000: 8.7 | Nests/100 sq km | B | Adult | Brooks, Alberta | Exposure Factor Datasets | Breeding | CANADA |
| Population Density | 1991: 32.6, 1993: 19.8, 1994: 17.2, 1997: 2.8, 1998: 5.7, 2000: 4.1 | Nests/100 sq km | B | Adult | Hanna, Alberta | Exposure Factor Datasets | Breeding | CANADA |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
|---|---|---|---|---|---|---|---|---|---|
| Dietary Composition | Arachnida: 7, Crustacea: <1, Insecta: see citation, Reptilia: <1, Aves: <1, Mammalia: see citation, Other vertebrates: <1 | Percent count of prey items | % | NR | Not Reported | 182 | Southern coastal Texas | Exposure Factor Datasets | USA |
| Dietary Composition | Arachnida: 1, Crustacea: <1, Insecta: see citation, Reptilia: 2, Aves: 9, Mammalia: see citation, Other vertebrates: 8 | Percent biomass of prey items | % | NR | Not Reported | 182 | Southern coastal Texas | Exposure Factor Datasets | USA |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Condition | Countries |
|---|---|---|---|---|---|---|---|---|---|
| Population Density | 6.9 | Breeding pairs/sq km | B | Adult | 264 | Cape Coral, Lee County | Exposure Factor Datasets | Breeding | USA |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
|---|---|---|---|---|---|---|---|---|
| Dietary Composition | See citation Table 1 | Vertebrate prey types by land-cover type | M | Adult | 18 | Between Alberta and Saskatchewan | Exposure Factor Datasets | CANADA |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
|---|---|---|---|---|---|---|---|---|---|
| Dietary Composition | Insecta: see citation, Arachnida: 9.1, Gastropoda: 0.8, Reptilia: 1.0, Aves: 2.9, Mammalia: 0.3 | Percent frequency of occurrence | % | NR | Not Reported | 55 | Marco Island, urban habitat | Exposure Factor Datasets | USA |
| Dietary Composition | Insecta: see citation, Arachnida: 8.3, Gastropoda: 1.7, Reptilia: 0, Aves: 0.7, Mammalia: 0.2 | Percent frequency of occurrence | % | NR | Not Reported | 29 | Rutland Ranch, rural habitat | Exposure Factor Datasets | USA |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
|---|---|---|---|---|---|---|---|---|---|
| Dietary Composition | Mice: 57.0, Insects: 31.6, Petrels 32.9, Auklet: 2.5, Unknown bird: 10.1 | Percent frequency of occurrence | % | NR | Not Reported | 79 | Southeast Farallon Island | Exposure Factor Datasets | USA |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sample Size | Location | Type | Countries |
|---|---|---|---|---|---|---|
| Population Density | See citation Figure 2 | Individuals/100ha | 60 | Eastern Colorado | Exposure Factor Datasets | USA |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
|---|---|---|---|---|---|---|---|---|---|
| Survival/ Mortality | Fledging: 0.78 [0.68-0.88 (95%)], Dispersal: 0.71 [0.58-0.86 (95% CI)], Pre-migration: 1.00 | Interval survival rate | % | B | Juvenile | Fledging:64, Dispersal: 49, Pre-migration: 18 | Regina Plain, Saskatchewan | Exposure Factor Datasets | CANADA |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sample Size | Location | Type | Countries |
|---|---|---|---|---|---|---|---|
| Dietary Composition | Mammals: 20.9, Birds: 0.6, Reptiles: 1.3, Chelicerates: 25.3, Lycosidae: 1.2, Bothriuridae: 24.1, Insects: 51.9 | Percent frequency of occurrence | % | 589 | Protected Natural Area Penı´nsula Valde´ s, Chubut, Argentina | Exposure Factor Datasets | ARGENTINA |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Location | Type | Countries | Error |
|---|---|---|---|---|---|---|---|---|---|
| Survival/ Mortality | >60% developed: 0.81, 40-60% developed: 0.62, 20-39% developed: 0.62, <20% developed: 0.81 | Estimated percent survival by percent urban housing development | % | M | Adult | Cape Coral, Lee County | Exposure Factor Datasets | USA | >60% developed: 0.04, 40-60% developed: 0.05, 20-39% developed: 0.05, <20% developed: 0.04 |
| Survival/ Mortality | >60% developed: 0.11, 40-60% developed: 0.28, 20-39% developed: 0.43, <20% developed: 0.18 | Estimated percent survival by percent urban housing development | % | B | Juvenile | Cape Coral, Lee County | Exposure Factor Datasets | USA | >60% developed: 0.02, 40-60% developed: 0.04, 20-39% developed: 0.08, <20% developed: 0.08 |
| Survival/ Mortality | >60% developed: 0.69, 40-60% developed: 0.52, 20-39% developed: 0.69, <20% developed: 0.69 | Estimated percent survival by percent urban housing development | % | F | Adult | Cape Coral, Lee County | Exposure Factor Datasets | USA | >60% developed: 0.04, 40-60% developed: 0.06, 20-39% developed: 0.04, <20% developed: 0.04 |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
|---|---|---|---|---|---|---|---|---|---|
| Dietary Composition | Invertebrates: 97, Vertebrates: 66 | Percent frequency of occurrence | % | NR | Not Reported | 426 | Nevada Test Site | Exposure Factor Datasets | USA |
| Dietary Composition | Invertebrates: 100, Vertebrates: 34 | Percent frequency of occurrence | % | NR | Not Reported | 213 | Nevada Test Site | Exposure Factor Datasets | USA |
| Dietary Composition | Invertebrates: 83, Vertebrates: 67 | Percent frequency of occurrence | % | NR | Not Reported | 186 | Nevada Test Site | Exposure Factor Datasets | USA |
| Dietary Composition | Invertebrates: 99, Vertebrates: 79 | Percent frequency of occurrence | % | NR | Not Reported | 806 | Nevada Test Site | Exposure Factor Datasets | USA |
| Dietary Composition | Invertebrates: 95, Vertebrates: 67 | Percent frequency of occurrence | % | NR | Not Reported | 1631 | Nevada Test Site | Exposure Factor Datasets | USA |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Location | Type | California Counties | Countries |
|---|---|---|---|---|---|---|
| Dietary Composition | See citation Figure 1 | Percent biomass/burrow | Exposure Factor Datasets | Santa Clara | USA |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Location | Type | Countries |
|---|---|---|---|---|---|---|---|
| Population Density | See citation Table1 | Breeding pairs/sq km | B | Adult | Northern Mojave Desert-eastern Sierra Nevada | Exposure Factor Datasets | USA |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties | Countries |
|---|---|---|---|---|---|---|---|---|---|---|
| Dietary Composition | Aranedia: 31.5, Coloptera: 51.9, Dermaptera: 64.8, Isopoda: 3.7, Lepidoptera: 14.8, Orthoptera: 98.2, Rodentia: 3.7, Solipugida: 40.7 | Percent frequency of occurrence in stomach contents | % | NR | Not Reported | 53 | Calipatria State Prison | Exposure Factor Datasets | Imperial | USA |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
|---|---|---|---|---|---|---|---|---|---|
| Dietary Composition | Baiomys taylori: 16, Reithrodontomys fulvescens: 11, Peromyscus: 7, Cryptotis parva: 6, Mus musculus: 6, Perognathus merriami: 3, Sigmodon hispidus: 1 |
Percent frequency of occurrence of mammalian species in pellets | % | NR | Not Reported | 182 | Southern Texas | Exposure Factor Datasets | USA |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Error |
|---|---|---|---|---|---|---|---|---|---|
| Survival/ Mortality | 0.12 | Estimated percent survival | % | F | Juvenile | 64 | Naval Air Station Lemoore | Exposure Factor Datasets | 0.025 |
| Survival/ Mortality | 0.557 | Estimated percent survival | % | F | Adult | 63 | Naval Air Station Lemoore | Exposure Factor Datasets | 0.071 |
| Survival/ Mortality | 0.277 | Estimated percent survival | % | F | Juvenile | 65 | Naval Air Station Lemoore | Exposure Factor Datasets | 0.1 |
| Survival/ Mortality | 0.575 | Estimated percent survival | % | F | Adult | 85 | Naval Air Station Lemoore | Exposure Factor Datasets | 0.065 |
| Survival/ Mortality | 0.294 | Estimated percent survival | % | F | Adult | 64 | Naval Air Station Lemoore | Exposure Factor Datasets | 0.053 |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties | Countries |
|---|---|---|---|---|---|---|---|---|---|---|
| Home Range | 98 [64-132 (95% CI)] | Mean by 95% fixed-kernel | ha | M | Adult | 19 | Naval Air Station Lemoore | Exposure Factor Datasets | Fresno | USA |
| Home Range | 189 [122-256 (95% CI)] | Mean by 100% MCP | ha | M | Adult | 22 | Naval Air Station Lemoore | Exposure Factor Datasets | Fresno | USA |
Clapper Rail (Rallus longirostris)
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries | Error |
|---|---|---|---|---|---|---|---|---|---|
| Survival/ Mortality | 0.368 | Mean annual survivial rate | NR | Adult | 11329 | Exposure Factor Datasets | USA | 0.07 | |
| Survival/ Mortality | 0.5 | Mean annual survivial rate | NR | Adult | 11329 | Exposure Factor Datasets | USA | 0.025 |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
|---|---|---|---|---|---|---|---|---|
| Population Density | 1999 EBS: 0.512, 1999 LBS: 0.507, 2000 EBS: 0.472, 2000 LBS: 0.523 | Individuals/ha | NR | Not Reported | 6629 | Colorado River Delta | Exposure Factor Datasets | MEXICO |
| Exposure Endpoint Type | Endpoint Value | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries | Error |
|---|---|---|---|---|---|---|---|---|---|
| Home Range | 0.28 | ha | B | Adult | 16 | LCP Superfund Site, Tutle River | Exposure Factor Datasets | USA | 0.8 |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Location | Type | Condition | Countries |
|---|---|---|---|---|---|---|---|---|
| Population Density | 90 [58-163 (95% CI)] | Breeding males/sq km | M | Adult | Sapelo Island salt marsh | Exposure Factor Datasets | Breeding | USA |
Brown Pelican (Pelecanus occidentalis)
| Exposure Endpoint Type | Endpoint Value | Life Cycle Stage | Sample Size | Location | Type | Countries |
|---|---|---|---|---|---|---|
| Hatching Success | 0 | Embryo | NR | Gaillard Island | Exposure Factor Datasets | USA |
| Hatching Success | 0.677 | Embryo | NR | Gaillard Island | Exposure Factor Datasets | USA |
| Hatching Success | 0.635 | Embryo | NR | Gaillard Island | Exposure Factor Datasets | USA |
| Hatching Success | 0.576 | Embryo | NR | Gaillard Island | Exposure Factor Datasets | USA |
| Hatching Success | 0.695 | Embryo | NR | Gaillard Island | Exposure Factor Datasets | USA |
| Hatching Success | 0.588 | Embryo | NR | Gaillard Island | Exposure Factor Datasets | USA |
| Hatching Success | 0.646 | Embryo | NR | Gaillard Island | Exposure Factor Datasets | USA |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Life Cycle Stage | Location | Type | Countries |
|---|---|---|---|---|---|---|
| Population Density | See citation Table 2 | Nests/ha/year | Adult | Coastal LA | Exposure Factor Datasets | USA |
| Population Density | See citation Table 2 | Colonies/ha/year | Both Adults and Juveniles | Coastal LA | Exposure Factor Datasets | USA |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Life Cycle Stage | Location | Type | Countries |
|---|---|---|---|---|---|---|
| Population Density | See citation Table 2 | Breeding pairs/ha | Adult | North central Chilean islands | Exposure Factor Datasets | CHILE |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sample Size | Location | Type | Countries |
|---|---|---|---|---|---|---|
| Dietary Composition | See citation Figure 3 | Proportion of anchovy:sardine | NR | Midriff Islands | Exposure Factor Datasets | MEXICO |
| Dietary Composition | 0.83 | Percentage of diet that is anchovy+sardine | NR | Midriff Islands | Exposure Factor Datasets | MEXICO |